Correlation of single band reflectance and Correlation of broad band vegetation indices and

tained in the first experiment were applied as forecast samples, then the data from second experiment were regarded as test samples.

3. RESULTS AND ANALYSIS

Spectral reflectance of water and Microcystic aeruginosa with different concentration were obtained by control experiments, under the condition of water disturbance and stationary. Spectral reflectance of bands whose wavelength located between 350nm-1000nm was used. Meanwhile two different narrow band vegetation indices and corresponding broad band vegeta- tion indices were calculated Table 1. Narrow band vegetation indices consisted of any two bands in the entire 651 narrow bands while broad band vegetation indices were the combina- tions of Landsat ETM+ NIR and RED bands. These specific spectral indices were:  Broad band ETM SR and NDVI indices;  Narrow SR and NDVI indices: any two bands in the entire 651 bands. Vegetation indices Definition SR Broad band NIR SR RED  Narrow band j SR ij i    NDVI Broad band RED RED NIR NDVI NIR    Narrow band j i NDVI ij j i        Table 1: Spectral vegetation indices used in this paper Where NIR = Landsat ETM+ B4 bands RED = Landsat ETM+ B3 bands.

3.1 Correlation of single band reflectance and

Microcystic aeruginosa chlorophyll-a Figure 1 shows the correlation coefficient r between single band reflectance and chlorophyll-a under the condition of water disturbance and stationary. The trend of r is very close to the Microcystic aeruginosa spec- tral reflectance. In the band intervals in which r decreased and increased quickly, Microcystic aeruginosa spectral reflectance has the similar change. In this area, reflectance is very sensitive to chlorophyll-a concentration. The location of 3 minimum reflectance is corresponding to 3 reflection troughs of Microcys- tic aeruginosa spectrum; the location of 3 maximum is corre- sponding to Microcystic aeruginosa spectral green range peak, secondary band peak, red edge respectively. Figure 1 Correlation coefficient between Microcystic aerugino- sa spectral reflectance and chlorophyll-a concentration

3.2 Correlation of broad band vegetation indices and

Mi- crocystic aeruginosa chlorophyll-a Under the condition of water disturbance and stationary, corre- lation coefficient r0.9 of Microcystic aeruginosa chloro- phyll-a with band 2, band 4 are both very high. At band 1 and band 3, correlation coefficient r0.5 is low under the condition of water disturbance. On the contrary, r is more than 0.85 under the condition of water stationary Figure 2. The independent variables include single band reflectance from 733nm to 794nm, ETM ’s band 4 reflectance whose central band is 835nm, the SR and NDVI consisted of ETM ’s band 3 4 and ETM ’s band 3 band 4 central bands. With these variables, linear prediction model of chlorophyll-a was constructed. The precision was evaluated by calculating determination coefficient and RMSE Table 2. prediction Test Independent variable condition function R 2 RMSE 799nm D y=8010.8x-112.55 0.9850 84.45 34.15 85.43 31.76 794nm S y =2355.8x-13.65 0.9903 835nm D y=10090x-116.83 0.9805 S y=2369.2x-2.2073 0.9912 This contribution has been peer-reviewed. doi:10.5194isprsarchives-XLI-B7-91-2016 94 ETM_B4 D y=9818x-116.6 0.9812 87.23 32.34 30.9 53.82 31.96 53.46 113.8 133.7 111.6 133 S y=2373x-3.518 0.9912 ETM_SR D y=341.4x-233.5 0.9928 S y=124.8x-98.87 0.9921 C_SR D y=364.19x-241.6 0.9956 S y=127.98x-98.01 0.9921 ETM_NDVI D y=1276.4x+125.7 0.8693 S y=985.4x-68.04 0.7193 C_NDVI D y=1293.5x+149.92 0.8776 S y=983.1x-56.508 0.7258 Table 2: linear model ETM_SR and ETM_NDVI were used to represent broad band indices and C_SR and C_NDVI to narrow band indices. Water disturbance and stationary was abbreviated as D and S respec- tively. The relation between chlorophyll-a real value Y and pre- dicted value y is: y a Y b   4 Where a= gain b = bias The RMSE is regarded as a scale used to compare each model ’s predictive ability. By comparing RMSE, under the condition of water disturbance, the predictive precision of SR model is high- er, even though the R 2 of single band model and SR model are both very high. Hence there is almost little discrepancy between narrow SR model and broad band SR model. Under the condi- tion of water stationary, SR model ’s predictive precision is low- er than that single band model ’s, where RMSE of SR model is 1.7 times higher than that of single band model. The predictive ability of ETM+ ’s band 4 model is close to which of 794nm model.

3.3 Correlation of narrow band vegetation indices and